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Pan WU Congqiang LIU Yuangen YANG Guoping ZHANG 《中国地球化学学报》2006,25(B08):42-42
Environmental impact resulting from mining activities is serious and ubiquitous all over the world, and it has become one of the important aspects in environmental geochemistry. The environment was seriously damaged by wastes from historical zinc smelting in Northwest Guizhou. The geochemical distributions of Pb and Zn in the different grain-size fractions of wastes indicate that the coarser particles show similar or even higher heavy metal concentrations than finer ones in the samples, although the concentrations of heavy metals tend generally to increase as the size fractions get finer. The heavy metal contents are very high, with maximum values of 31631, 57178, 2367 and 311.5 mg/kg for Pb, Zn, Cu and Cd, respectively. It is also shown that the residual fraction of Pb is less than that of Zn, accounting for 0.39%-15.75% and 14.3%-46.2%, respectively, of the total, and this is likely relative to Zn-silicate minerals formed from smelting. Although the relative partitioning of Pb and Zn is very low (0.03%- 1.3.% for Pb; 0.03% -3.3% for Zn), the exchangeable fraction of the waste contains large amounts of heavy metals (1.5%-385 μg/g for Pb; 3-590 μg/g for Zn). Heavy metals in exchangeable forms have the highest solubility to give the highest potential bioavailability in contrast to other chemical forms. Mineralogical study indicates that the wastes were found to be highly heterogeneous materials, dominated by quartz, feldspar, carbonatite, iron or/and aluminum vitric compounds and a few secondary mineral phases, and their contents vary with the type of smelting wastes. The secondary minerals formed from smelting and sequentially weathering are the major chemical phase for heavy metals. Complex composition of many phases and substitution of elements suggested that many of the phases were found to be non-stoichiometric compounds. Pb was found to be the main Pb phase in the wastes by precipitation or/and adsorption. 相似文献
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The Sepetiba Bay is a shallow water body semi enclosed located on the west side of Rio de Janeiro City. Almost 80% of flesh water discharge, from the St Francisco canal, coming from the northern side of the bay develops an estuarine environment. Fishing and tourism are some of the most important economic activities in the area. During 35 years a zinc/cadmium smelter has polluted the bay. The objective of this investigation is to demonstrate the diagenetic processes and cadmium remobilization into pore water from the contaminated sediments. Two sites were selected to compare diagenetic processes. Site P1 is located next to domestic effluents discharge into the bay and approximately 20km away from the smelter. Site P2 is located near the same smelter and next to the Mazomba estuary, which is not influenced directly by domestic effluents. Peeper samplers of 25 cells with a resolution of 2.5 cm were deployed at both the sites. After a 3-weeks period of equilibrium, the pore waters were separated from the cells and analyzed immediately (within 24 h) for alkalinity, NH3 and reactive soluble phosphorus on a spectrophotometer. An ICP-AESΣH2S spectrometer was used to analyze Na, Mg, Li, Ba, Sr, Si, Fe and Mn. Total and labile dissolved Cd in pore waters were determined by differential-pulse stripping voltametry. The dissolved constituents in the pore waters have shown that the intensities of diagenetic reactions are different between sites. The reactions are stronger at site P1 site than at site P2, especially between 7.5 cm and 22.5 cm, which is evident by the organic rich sediment. 相似文献
478.
对2-(5-氯-2-吡啶偶氨)-5-二乙基氨基酚(5-Cl-DEPAP)作锌的络合滴定指示剂进行了实验。在pH5.5的HAc—NaAc介质中,以5-Cl-DEPAP作指示剂,EDTA标准溶液滴定锌,溶液颜色由紫红色变为亮黄色,终点变化敏锐,易于观察,锌量在0-25mg与EDTA消耗量成正比。方法用于化学试剂和铝合金中锌的测定,5次测定的RSD小于0.1%。结果表明,5-Cl-DEPAP符合络合滴定对指示剂的基本要求,扩大了该试剂的应用范围。 相似文献
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通过对桂平市四德铅-锌-铜矿床的区域地质背景、矿床地质特征、矿物组合及结构构造、成矿物质来源等的研究,初步认为其矿床类型为热水沉积型铅-锌-铜矿床。通过对该矿床的成矿条件、地球物理、地球化学特征等的分析,认为该矿床具大型规模的成矿前景。 相似文献
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铜和锌是普遍存于对虾养殖池塘中的重金属污染物质,查明铜和锌在水环境中的迁移规律对有效防控养殖环境铜和锌污染以及对虾健康养殖具有重要意义。作者在不同铜和锌暴露时间下测定了条纹小环藻(Cyclotella striata)铜和锌富集富集率,研究了条纹小环藻铜和锌富集动力学,并探讨了温度、盐度和光照度对条纹小环藻铜和锌富集的影响。结果表明:条纹小环藻铜和锌富集过程分为快速、慢速和富集平衡3个阶段。快速富集在30 min内完成,富集率可达70%以上;慢速富集大约分别在4 h和6 h完成,富集率均可达90%;以后达到富集平衡。温度、盐度和光照度对条纹小环藻铜和锌富集有显著影响。条纹小环藻铜和锌富集的最适温度范围分别为25~35℃和15~35℃,盐度范围分别为20~35和25~30,光照度均为3000~7500 lx。条纹小环藻铜和锌富集的光饱和点为3000 lx。条纹小环藻在亚热带虾池中对铜和锌均具有较强的富集能力。 相似文献